Name: Potential Role of Arbuscular mycorrhizal fungi in Phytoremediation
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Author: Sadia Kanwal
ISBN: 978-3-668-26482-3

The increase of metals pollution in soil is a worldwide problem that effects the health of humans and environment. The use of green technology such as phytoremediation is one the environmental friendly technique, in which plants and other microbes are used to reduce the level of metals contaminants in soil and lower its uptake towards plants tissues.

Studies reported a number of cereal crops such as wheat and medicinal plants like alfalfa accumulate heavy metals in their tissues at higher concentrations. In the present study, we investigated the effect of arbuscular mycorrhizal fungi (AMF) on wheat and alfalfa plants with the increase of zinc (Zn) and cadmium (Cd) concentrations in soil. After eight weeks of pot experiment, roots colonization, shoot and root biomass, growth, heavy metals contents and other biochemical parameters were assessed.

The results indicated mycorrhizal inoculated (M) plants performed better at moderate Zn and Cd concentrations. In addition, higher phosphorus contents were observed in M treated plants as compared to NM plants. Results indicated that AMF inoculum exhibit different tolerance strategies to reduce metals toxicity in host plants. The effective mycorrhizal symbiosis was observed with wheat and alfalfa plants and can be useful for phytostabilization of metals contaminated soils which can play a vital role in increase of plants productivity and safety.

Excerpt

Role of arbuscular mycorrhizal fungi in phytoremediation of heavy metals and effects on growth and biochemical activities of wheat (Triticum aestivum L.) plants in Zn contaminated soils 11
Abstract
1 Introduction
2 Experimental methodology
2.1 Experimental design
2.2 Soil preparation
2.3 Use of AMF Glomus species
2.4 Disinfection and germination of wheat seeds
2.5 Seeds sowing and harvesting of plants
2.6 Mycorrhizal colonization of roots
2.7 Biomass of plants
2.8 Plant growth
2.9 Metal contents in plants
2.10 Biochemical contents of plants
2.11 Antioxidant enzymes activity in plants
2.12 Quality Control (QC/QA) analysis
2.13 Statistical Analysis
3 Results
3.1 Roots mycorrhizal colonization
3.2 Plant Growth and Biomass
3.3 Macro and micro-nutrients uptake
3.4 Phosphorus (P) content in plant tissues
3.5 Zinc uptake in plants tissues
3.6 Biochemical contents in plant tissues
3.7 Antioxidant enzyme activities in plants
4 Discussion
Conclusion
References

Effects of arbuscular mycorrhizal fungi on wheat growth, physiology, nutrition and cadmium uptake under increasing cadmium stress
Abstract
1 Introduction
2 Materials and Methods
2.1 Plant materials
2.2 Preparation of soil
2.3 Fungal inoculum
2.4 Pot experiment and growth conditions
2.5 Plant measurements and analysis
3 Results
3.1 Plant biomass and Mycorrhizal colonization
3.2 Effect on plant growth
3.3 Plant Phosphorus (P) uptake
3.4 Cd uptake in wheat plants
3.5 Plant nutrient contents
3.6 Plant biochemical Analyses
3.7 Antioxidant enzyme activities
4 Discussion
Conclusion
References

Effects of arbuscular mycorrhiza fungi on metals uptake, physiological and biochemical response of Medicago Sativa l. with increasing Zn and Cd concentrations in soil
Abstract
1 Introduction
2 Materials and Methods
2.1 Experimental design and soil preparation
2.2 Inoculum of Glomus species:
2.3 Sterilization of Alfalfa seeds:
2.4 Evaluation of mycorrhizal colonization:
2.5 Plant growth:
2.6 Plant biomass:
2.7 Analytical determinations
2.8 Quality Control Analysis:
2.9 Statistical analysis:
3 RESULTS
3.1 Mycorrhizal colonization of roots
3.2 Plant Growth and Biomass
3.3 Plant Nutrient contents
3.4 Plant Phosphorus (P) uptake
3.5 Zinc and Cd uptake in Alfalfa plants
3.6 Effects of metals concentrations on plants biochemical activities
3.7 Effects of metals on plants antioxidant enzyme activities
4 Discussion
4.1. Effect of AMF inoculation on alfalfa growth, biomass and colonization under Zn and Cd toxicity
4.2 Effect of AMF on Zn and Cd uptake in Alfalfa plants
4.3 Effects of AMF on nutrients uptake and biochemical contents under Zinc and Cd toxicity
Concluding Remarks
References

ACKNOWLEDGEMENT

All admires to Almighty Allah, who gave me the ability and strength to complete this research work, and all respects and grandeurs for our Holy Prophet (Peace Be Upon Him and His Progeny), who is everlasting source of knowledge and wisdom for humanity.

I am deeply and forever indebted to my parents for their love, support and encouragement throughout my entire life. I am also very grateful to my beloved brothers Faisal, Bilal, Usman and to my only sister Maryam for their moral support and prayers they had made for my success. May ALLAH ALMIGHTY infuse me with the energy to fulfill their noble inspirations and expectations and further edify my compete.

Sadia Kanwal

LIST OF Abbreviations

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Part 1 Role of arbuscular mycorrhizal fungi in phytoremediation of heavy metals and effects on growth and biochemical activities of wheat (Triticum aestivum L.) plants in Zn contaminated soils

Abstract

The increase of metals pollution in soil is a worldwide problem that effects the health of humans and environment. The use of green technology such as phytoremediation is one the environmental friendly technique, in which plants and other microbes are used to reduce the level of metals contaminants in soil and lower its uptake towards plants tissues. Studies reported a number of cereal crops such as wheat accumulate heavy metals in their tissues at higher concentrations. In the present study, we investigated the effect of arbuscular mycorrhizal fungi (AMF) on wheat plants with the increase of three different zinc (Zn) concentrations (0, 100, 300, 900 mgkg-1) in soil. After eight weeks of pot experiment, roots colonization, shoot and root biomass, growth, heavy metals contents and other biochemical parameters were assessed. The results indicated mycorrhizal inoculated (M) plants performed better at moderate Zn concentrations (300 mgkg-1). In AMF associated plants, Zn contents were lower in shoot part of plants as compared to roots. In addition, higher P contents were observed in M treated plants as compared to NM plants. The decrease of nutrient contents, growth and antioxidant enzymatic activities were found at highest applied Zn concentrations (900 mgkg-1). Results indicated that AMF inoculum exhibit different tolerance strategies to reduce metals toxicity in host plants. The effective mycorrhizal symbiosis was observed with wheat plants and can be useful for phytostabilization of Zn contaminated soils which can play a vital role in increase of food productivity and safety.

1 Introduction

Soil contamination with heavy metals is the most challenging problem nowadays that is the consequence of increasing emissions from both natural and anthropogenic sources. The increase level of metals threatens the quality of food and management of sustainable environment (Thounaojam et al., 2012). Among the metals, Zn is one of the essential micronutrients required by plants in adequate quantities and play an important role in numerous structural and metabolic processes of plants. Excessive concentrations of Zn in soil increase the plants toxicity and consequently decrease the plant growth, yield and level of reactive oxygen species (ROS) (Sgherri et al., 2002).

Nowadays, the useful function of mycorrhiza in decrease of phytotoxicity has been generally known. The mechanism of phytoremediation can be increased by using arbuscular mycorrhizal fungi (AMF) in soil. AMF are symbionts colonized with plant roots found in many plant species and contaminated soils with heavy metals. AMF immobilize Zn in plant roots which decrease the harmful effects of metals on plants physiological and metabolic functions. Several studies indicated that plants grow in the presence of AMF have developed a variety of useful mechanisms that reduce the metals uptake in plants, increase the nutrient contents and form an efficient symbiotic relationship by inducing several mycorrhizal structures inside plant roots like arbuscules or vesicles (Gohre et al., 2006).

Despite the importance of wheat crop in agriculture, no detailed information is available about biochemical alterations induced in the crop due to excessive metals concentrations (Mallick et al., 2011). In addition, little information is available with respect to association of mycorrhiza with wheat plants under toxic Zn concentrations, and the influence of mycorrhization on physiological and biochemical functions of wheat. The purpose of the study was to investigate the effects of mycorrhizal inoculation on growth, nutrients and biochemical contents of wheat plants grown in low (100 mgkg-1), moderate (300 mgkg-1) and high (900 mgkg-1) Zn concentrations. The hypothesis of the study was that use of AMF inoculum in metals contaminated soils immobilize the metals contents in plants roots, increase growth, nutrients contents and other biochemical activities in plant tissues enhance the quality and food productivity.

2 Experimental methodology

2.1 Experimental design

The pot experiment was conducted under controlled laboratory conditions. The treatments consist of a) AMF inoculated wheat plants and b) non-inoculated plants; with different applied Zn concentrations (0, 100, 300, 900 mgkg-1) in soil. All the treatments were installed in replicates, consisting of six replicates for each treatment, with the total of 48 pots.

2.2 Soil preparation

Soil and sand were collected to install the experiment from the vicinity of Quaid-i-Azam University, Islamabad, Pakistan. The average temperature of the area was 20-25oC. The soil and sand samples were air-dried, and sieved with 2 mm sieve to remove any debris from the samples. The chemical analysis of soil samples was carried out before the start of experiment. Soil was chemically characterized with a pH (6.7), T. Phosphorus (4.3 mgkg-1), T. Potassium (19.5 mgkg-1), Calcium (34.45 mgkg-1), Magnesium (42.50 mgkg-1), Extractable nitrate nitrogen (1.04 mgkg-1), Extractable potassium (1.45 mgkg-1), Extractable phosphorus (1.53 mgkg-1), Zinc (1.50 mgkg-1), Nickel (1.33 mgkg-1), Copper (30.3 mgkg-1), Cadmium (1.60 mgkg-1), Iron (28.51 mgkg-1), Lead (1.6 mgkg-1), Chromium (4.25 mgkg-1) and Manganese (10.4 mgkg-1) respectively. Then, soil and sand were autoclaved twice for one hour at 120oC to remove any local AMF spores. After autoclaving, soil and sand combined with the ratio of 1:3 and used in pots to grow the wheat plants. Plants were treated with low (100), moderate (300) and high (900) concentrations of Zn (mgkg-1) in soil.

2.3 Use of AMF Glomus species

Glomus species used as AMF fungal inoculum in the pot experiment and mixed with the soil. The inoculum was obtained from the company in France. The two pot experiments with wheat plants were installed; 1. with the application of AMF fungal inoculum and applied Zn concentrations (0, 100, 300, 900 mgkg-1) in soil. 2. with the application of different Zn concentrations (0, 100, 300, 900 mgkg-1) in soil. About 50 g of AMF inoculum were used in M associated wheat experiment 1 (mycorrhizal experiment). There were no inoculation of mycorrhizal spores in the second experiment (non-mycorrhizal experiment).

2.4 Disinfection and germination of wheat seeds

Seeds of wheat (Triticum aestivum L.) were taken from Department of Crop Science, National Agriculture Research Centre, Islamabad. Seeds were sterilized by using Clorox, and soaked for about 10 minutes. After sterilization, seeds were appropriately washed with Milli-Q water several times and then placed on petri dishes in dark (for about 2 days) for germination.

2.5 Seeds sowing and harvesting of plants

After seed germination, seedlings were sown in pots and grown for 8 weeks in a greenhouse with 16 hours daylight (20–22oC). About 5 seedlings were grown in each pot. Proper light (12 hours) and temperature conditions (25-30oC) and water conditions (on daily basis) were maintained during the experiment. Ashton nutrient solution (10 mL) was provided to plants once in a week. There were about 6 replicates for each treatment. Plants were harvested after 8 weeks of growing in pots.

2.6 Mycorrhizal colonization of roots

After harvesting of plants, roots and shoots were separated. Fresh roots samples were used for assessment of mycorrhizal colonization and line intersect method was used to evaluate the percentage of colonization (Giovannetti et al., 1980). For each treatment, mycorrhizal colonization percentage were calculated.

2.7 Biomass of plants

Plants roots and shoots were washed with tap water to remove any soil particles. Then, fresh weights of plants tissues were measured. After measurement of fresh weight, samples were placed in the oven for drying and then determine dry weight. Biomass of plants tissues were assessed by calculating the difference between fresh weight and dry weight of the samples.

2.8 Plant growth

Shoot and root growth in M and NM plants were measured separately. Growth was measured by recording parameters including length, breadth and area of the plants samples. Vernier caliper (ECV150C, China) was used to measure the length and diameter of plant tissues.

2.9 Metal contents in plants

Plants tissues (shoots and roots) were analyzed separately for macro and micronutrient contents. Samples were dried, grind, digested in HNO3 and H2O2 by using microwave digestion system (CEM-MDS 2000). After digestion, plants shoot and roots were analyzed for metals contents including macro (Mg, K, Na, Ca) and micro-nutrient contents (Cr, Cu, Ni, Mn, Zn, Pb, Fe, Cd) by using atomic absorption spectrophotometer (Varian FAAS-240). Plant tissues were also analyzed for total phosphorus (Ryan et al., 2001) and nitrogen contents (Van and Walinge, 1973).

2.10 Biochemical contents of plants

Fresh leaves of wheat plants were assessed for total chlorophyll, carotene (Duxbury et al., 1956), proline (Bates et al., 1973), sugar (Dubois et al., 1956) and protein contents (Lowry et al., 1951).

2.11 Antioxidant enzymes activity in plants

Fresh samples of plants were analyzed for antioxidant enzymatic activities. Superoxide dismutase (SOD), Peroxidase (POD), Catalase (CAT), and Ascorbate peroxidase (APX) activities were analyzed by using spectrophotometer. SOD in fresh leaves were analyzed by using the method of (Beauchamp et al., 1973). POD activity was evaluated by using the procedure of (Gorin and Heidema, 1976). CAT and APX activity were determined by using the method of (Goel et al., 2003) and (Nakano and Asada, 1981).

2.12 Quality Control (QC/QA) analysis

Quality of analysis were measured by performing analysis in replicates (n=6) and by repeated measurements of each sample. To verify the accuracy of procedures, standard reference soil (NIST, 2709 San Joaquin) and plant materials (NIST, 1547 Peach leave) of National Institute of science and Technology were included in each sample batch. Metals recovery were about 99%. After measurement of five samples, blank samples were run.

2.13 Statistical Analysis

All the parameters (mycorrhizal colonization, metals contents, growth parameters, biochemical contents, antioxidant enzyme activities) in M and NM treatments were analyzed by two way analysis of variance (ANOVA) using statistix (version 8.1) software. In all treatments and analysis, Tukey test was used for comparison of means at 5% level.

3 Results

3.1 Roots mycorrhizal colonization

Fig 1 shows the colonization of mycorrhizal structures with plants roots. No colonization was observed in non-mycorrhizal (NM) treatments. The AMF plants showed higher percentage of colonization in all treatments. The presence of M colonization with plant roots indicated the existence of mycorrhizal structures (arbuscules and hyphae). From the results, it is clear that the symbiotic relationship between wheat and mycorrhizal inoculum can be established under higher zinc concentrations. It is observed from the results that highest percentage of M colonization (72.16%) was observed at lowest Zn applied concentration (100 mgkg-1), while the lowest M colonization (67.56%) was observed at highest applied Zn concentration (900 mgkg-1). The results indicated that excessive Zn concentrations in soil negatively effects mycorrhizal colonization of plants roots.

3.2 Plant Growth and Biomass

The effect of increasing Zn concentrations (100, 300, 900 mgkg-1) on physiological parameters (length, breadth, area) were examined in M and NM associated wheat plants (Fig. 2). It was observed from the results of present study that M inoculation had positive effects on growth and biomass of wheat plants under increasing Zn concentrations as compared to NM wheat plants. Fig. 2 (a, b) indicates AMF associated wheat plants showed significantly higher shoots and root biomass as compared to plants not inoculated with AMF. This was also observed from the results that excessive Zn concentrations badly effects the wheat plants in both M and NM plants. In 100 and 300 mgkg-1 soil, a significant increase (P <0.05) was noticed in shoot and root biomass of mycorrhizal associated plants, while the lower trend was observed at highest applied Zn concentration (900 mgkg-1).

Fig. 2 (c-d) shows that increasing concentrations of Zn effects the length of plants tissues in M and NM inoculated plants. Results showed that at high Zn concentration (900 mgkg-1) cause in reduction of both shoot and root growth in M and NM plants. However, significant increase in growth was observed in M associated wheat plants at 100 and 300 mgkg_1 applied Zn concentrations. Overall, higher shoot and root length was observed in M wheat plants as compared to NM plants at lower and moderate Zn applied concentrations. Therefore, all the results shows that mycorrhizal associated plants showed better growth at Zn concentrations (0, 100, 300 mgkg-1) in soil. However, at maximum Zn concentration (900 mgkg-1), reduction in plant growth was observed in both M and NM associated plants.

3.3 Macro and micro-nutrients uptake

Table 1 and 2 shows macro-nutrients and micro-nutrients contents of wheat plants (shoot and root) in both M and NM treatments with increasing Zn concentrations. Overall, in M associated treatments, improved nutrients contents (N, P, K, Ca, Mg, Na, Fe, Cu) were recorded. However, significant variations were noticed for nutrients uptake (K, P, Na, N, Cu, Mn) in both M and NM plants. However, non-significant results were observed for Ca and Mg at each Zn concentration. Excessive Zn addition level (900 mg kg-1) had a harmful effect on nutrients uptake, as there was a significant decline of nutrients contents observed in both M and NM treatments.

The results of the experiment revealed that mycorrhization significantly effects the nutrient contents of wheat plants, improving the concentrations of P, K, N, Ca, Mg, Na, Cu and Ni but reducing the Mn and Fe contents in shoot part of plants. The increase of N, Cu, Mn and Ni were observed in roots of M plants in contrast to NM wheat plants. In comparison of shoot part, increased nutrient contents N, Ca, Na, K and Ni were observed in roots tissue of wheat under Zn applied levels (Table 2).

3.4 Phosphorus (P) content in plant tissues

The results of Fig. 3 (a, b) indicated that significantly higher P contents were observed in M associated plants at 100 and 300 mgkg-1 of applied Zn concentration in soil. However, lower P contents was observed at highest applied Zn concentrations (900 mgkg-1) in M treatments. It was observed from the results of present study, shoots of M associated plants accumulated higher P level than roots at lower (100 mgkg-1) and moderate (300 mgkg-1) applied Zn levels. At highest applied Zn concentrations (900 mg kg-1), P contents were significantly lower in both M and NM plants.

3.5 Zinc uptake in plants tissues

Fig. 4 a and 4b shows the uptake of Zn in shoots and roots of plants in both M and NM associated wheat plants at each applied Zn concentrations. The results indicated that Zn contents increased in plants tissues as the concentration of Zn was increased in the soil. In NM treatments, more Zn uptake was recorded in wheat tissues (shoot and root) as the Zn contents increased in soil (100, 300, 900 mgkg-1).

When no Zn was applied (0 application level), the non-significant results were observed in both M and NM treated plants. The results showed that in NM plants, as the Zn concentration increased in the soil, more Zn was accumulated in shoot part as compared to root part of plants. The higher Zn concentration was observed at 900 mgkg-1 in both M and NM treated plants.

3.6 Biochemical contents in plant tissues

Fig 5 a, b and c shows the chlorophyll and carotene of M and NM wheat plants. The results showed that in M plants, the chlorophyll (a, b) and carotene contents (c) observed were significantly higher in contrast with NM associated wheat plants at all applied Zn concentrations (0, 100, 300, 900 mgkg-1). At Zn concentration of 100 mgkg-1, the more chlorophyll a and b were recorded in both treatments. At highest Zn concentration (900 mgkg-1), lowest chlorophyll a and b contents were observed in M and NM associated wheat plants.

Fig 5d shows content of proline in M and NM inoculated wheat plants as the applied Zn concentration increased (0, 100, 300, 900 mgkg-1) in soil. It was observed from the results of present study that proline contents were significantly increased as the concentration of Zn increased in the soil. The results showed that proline content was higher in NM plants as compared to M plants. But the trends observed were same at all applied Zn concentrations.

Fig 5e shows contents of sugar in M and NM treatments under increasing Zn levels in soil. The results indicated that M plants showed significantly higher sugar contents as compared to NM plants tissues. Total sugar contents were improved in plants shoot and roots as the Zn concentration increased in soil (100, 300 mgkg-1). The decrease of sugar content was observed at highest applied Zn level (900 mgkg-1) in both M and NM associated wheat plants.

3.7 Antioxidant enzyme activities in plants

Fig 6 shows the trends of antioxidant enzymes (SOD, CAT, APX, POD) activities in shoot and root of both M and NM associated wheat plants under increasing Zn concentrations (0, 100, 300, 900 mgkg-1). Fig 6a shows that in NM associated treatments, the contents of SOD was low as compared to M plants and a slight increase in concentration was observed as more zinc concentration introduced in soil. The highest activity of SOD in M plants was observed at 300 mgkg-1.

Fig 6b shows in M inoculated plants, Zn exposure cause a significant reduction of POD content at Zn concentration of 900 mgkg-1. Fig 6c shows CAT activity improved as the concentration of Zn increased in both NM and M treated plants. At higher Zn application level (900 mgkg-1), the decrease CAT activity was observed. Fig 6d shows APX activity was enhanced as the Zn application increased in soil. The observed trends were same for both APX and CAT in M treated plants.

4 Discussion

AMF can reduce Zn toxicity in plant species and effects positively on growth of plants in comparison to non-AMF plants (Arriagada et al., 2005). The results indicated AMF inoculated wheat plants with different Zn concentrations showed increased plant growth than NM treated plants. However, Zn concentrations >300mg/kg may inhibit root and shoot growth showing Zn phytotoxicity. Zn is essential nutrient but more concentration of Zn (< 300 mg/kg) can decrease plant growth and in some cases cause to inhibition of plant growth (Gratao et al., 2005). This might be due to the fact that less Zn concentration can cause inhibition of plants for further growth. The other possible reason is more pH of soil (7.8) may cause Zn availability to plant tissues become immobilized and reduce its uptake to shoot and roots.

As Zn concentration increased in soil, percentage of mycorrhizal colonization in roots of wheat plants was significantly reduced. Several authors described the reduction of mycorrhizal colonization with plants roots is due to increase toxicity of heavy metals. Some studies reported that mycorrhizal colonization do not decrease in plants growing with high metal contents (Li et al., 2011). This might be due to the fact that species of mycorrhiza isolated from heavy metals polluted soil are more tolerant and resistant to metals as compared to the species that are less tolerant (Leung et al., 2006).

In the present study, Zn uptake was increased in plants shoots and roots at lowest applied Zn levels and the defensive mechanism of mycorrhizal fungi in plants tissues with higher Zn concentrations were recorded. NM treated plants showed higher Zn concentrations in their shoots which cause reduction of plants yield. AMF fungus protects the plants from moderate Zn contamination by immobilizing Zn in the fungal mycelium. This may be due to the mechanism that mycorrhizal plants might lower the uptake of heavy metals contents. Mycorrhizal association also increased uptake of important nutrients especially P. The increase of P content and other nutrients such as N, Mg, Ca and K in M plants also enhanced the productivity of plants (Chen et al., 2003). The improvement of P contents in AMF associated plants is due to its increase uptake through mycorrhizal structures i.e. arbuscules and vesicles (Smith and Read, 1997).

The significant nutrients deficiency was recorded in NM treated wheat plants grown in soil with increased Zn concentrations as compared to M treated plants. The reduced K uptake in plant shoot was observed as the Zn concentrations increased in NM treated wheat plants. This phenomenon might be due to removal of K in roots at higher Zn concentrations and also due to membrane rupture of plants that cause K leakage (Bonnet et al., 2000).

The increase of metals toxicity also increased proline contents and different amino acids as the metals concentrations increased in the soil. This can be the protective mechanism of plants tissues under high metals stress conditions. One mechanism of proline is to decrease the production of free radicals as the metals concentrations increased in soil (Mittler et al., 2002). The increase of proline contents in plants shoot is also one of the indication of increased metal toxicity. Antioxidant enzymes (CAT, APX and SOD) play a vital role in increasing defensive mechanisms towards more ROS production (Foyer et al., 2005a). It is suggested from the results of present study that AMF is able to maintain mycorrhizal symbiosis in Zn toxic soils and significantly increase the plant growth, productivity and nutrient contents.

Conclusion

The study concluded that inoculation of mycorrhizal fungal species in plants had useful impacts on increasing the growth, biomass, yield, and nutrient contents of plants. Better growth, biomass, improved nutrients uptake and higher yields were recorded in M treated plants as compared to NM treated plants. However, in M plants, the Zn contents were lower in shoot at the highest applied Zn levels (900 mgkg-1). This decrease of Zn transfer from soil to shoot tissue shows the ability of AMF inoculum to alleviate metal toxicity in wheat plant. In general, AMF protected the wheat plants against metal toxicity and also improved the nutrients contents of plants. The importance of mycorrhization for wheat plants under high Zn concentrations were observed. As levels of heavy metals is increasing due to increase use of sewage sludge in agriculture, and also due to industrial emissions that cause to contaminate the agricultural soils. The useful application of mycorrhizal association for cereal crops in field can improve agricultural ecosystem. Furthermore, experiments under field conditions should be employed to study the extent to which mycorrhizal fungi can alleviate Zn plant toxicity.

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Figure 1